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ARCHIVED REPORTS_XR0002277
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545202
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ARCHIVED REPORTS_XR0002277
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Last modified
1/27/2020 11:05:55 AM
Creation date
1/27/2020 10:00:52 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002277
RECORD_ID
PR0545202
PE
3528
FACILITY_ID
FA0003124
FACILITY_NAME
7-ELEVEN INC. STORE #20304
STREET_NUMBER
455
Direction
W
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
455 W GRANT LINE RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Quarterly Monitoring and Sampling Activities March 18, 1993 <br /> Southland Site No. 20304, 455 Grant Line Rd., Tracy, CA 2 <br /> Monitoring Well Sampling <br /> After well monitoring, groundwater samples were collected from the 14 monitoring wells according to <br /> Groundwater Technology, Inc., Standard Operating Procedures (SOPs) (Attachment 3). The ground- <br /> water samples, a trip blank, and a rinsate blank were submitted under chain-of-custody protocol to GTEL <br /> Environmental Laboratories (GTEL) in Concord, California. Each sample was analyzed for benzene, <br /> toluene, ethylbenzene, and xylenes (BTEX), and for total petroleum hydrocarbons-as-gasoline (rPH-G) <br /> using Environmental Protection Agency (EPA) Methods 5030/8020 and 8015. Twelve samples were also <br /> analyzed for fecal coliform bacteria. Figure 2 illustrates the distribution of benzene and TPH-G. Table 2 <br /> summarizes the analytical results of this sampling event and the historical analytical data. Fecal coliform <br /> bacteria were detected in groundwater samples from four wells (MW-1, MW-2, MW-8, and MWA5), with <br /> the highest concentration (less that 23.0 organisms per 100 milliliters) near well MW-8. The laboratory <br /> analytical reports and the chain-of-custody records for the December 28, 1993, samples are included in <br /> Attachment 4. <br /> Conclusions and Recommendations <br /> ■ Historically, wells MW-2 and MW-3 reported hydrocarbon concentrations below method <br /> detection limits. Detection of hydrocarbons in wells MW-2 and MW-3 during the <br /> December 28, 1992, sampling may be because more sensitive detection limits were <br /> provided by GTEL and the rising groundwater levels. <br /> 0 The anomalous groundwater elevations in wells MW-9 and MW-10 may be caused by <br /> the shallower screening interval used in these two wells. The different elevations <br /> measured in wells MW-11 and MW-2 may be because of changes in subsurface <br /> lithologies and/or man-made conduits affecting groundwater elevations. <br /> ■ The presence of coliform bacteria appears to be associated with a former sewer leak <br /> near wells MW-8 and MW-9. Overall the concentrations appear to be dropping. Off-site <br /> concentrations may be because of leaks from the public sewer system. <br /> Based on the groundwater monitoring and analytical data collected to date, Groundwater Technology <br /> recommends that quarterly monitoring continue during 1993. Proposed groundwater remediation will <br /> reduce migration of the dissolved-phase hydrocarbon plume. <br /> r <br /> R3767A1.MK p <br /> J, GROUNDWATER <br /> '�J(jI TECHNOLOGY,INC. <br />
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